process for removing sodium sulphate from an aqueous citrate, adipate or phosphate buffer solution used for absorption of SO2 from exhaust gases, by evaporating an aqueous buffer solution at atmospheric pressure at a temperature near its boiling point, thereafter separating the precipitated sodium sulphate and optionally subjecting it to further treatment to recover accompanying buffer salt. The further treatment may consist in a treatment of the precipitated sodium sulphate together with accompanying buffer salt with water at elevated temperature. The solution which is then obtained is mixed with the rest of the buffer solution.

Patent
   5108625
Priority
Feb 24 1988
Filed
Aug 22 1990
Issued
Apr 28 1992
Expiry
Apr 28 2009
Assg.orig
Entity
Large
4
11
all paid
1. A process for removing sodium sulphate from an aqueous citrate, adipate or phosphate buffer solution used for absorption of SO2 from exhaust gases, which comprises evaporating the aqueous buffer solution at a temperature close to its normal boiling point to precipitate sodium sulphate, and separating the precipitated sodium sulphate from the buffer solution, and optionally subjecting the separated sodium sulphate to a treatment with water at elevated temperature to dissolve and recover accompanying buffer salts which are conveyed back to the buffer solution.
2. The process according to claim 1, wherein a citrate buffer solution used for absorption of SO2 is subjected to a stripping of SO2 with steam, prior to the evaporation and separation.
3. The process according to claim 1, wherein an adipate buffer solution used for absorption of SO2 is subjected to a stripping of SO2 with steam and subsequent cooling for precipitation of free adipic acid, prior to the evaporation and separation.
4. The process according to claim 1, wherein a phosphate buffer solution is evaporated directly after the SO2 absorption.
5. The process according to claim 4, wherein the phosphate buffer solution is evaporated in two or more steps, a salt which primarily consists of sodium sulphate being precipitated in a first step, and a salt which in addition to sodium sulphate also contains phosphate buffer salts being precipitated in the subsequent step or steps, said salt precipitated in said subsequent step or steps being subjected to a treatment with water at elevated temperature to dissolve and recover phosphate buffer salts.
6. The process according to any one of claims 1-5, wherein the buffer solution after SO2 absorption is separated into a first stream containing a minor part of the buffer solution and a second stream containing a major part of the buffer solution, said first stream is subjected to said process for removing sodium sulfate, and the resultant purified buffer solution is mixed with said second stream so that the concentration of sodium sulphate in the resultant mixture is kept at no greater than 2.0M.
7. The process according to claim 6, wherein the concentration of sodium sulphate in said resultant mixture is kept in the range 0.1-2.0M.

This invention relates to a process for purifying aqueous buffer solutions used for absorption of sulphur dioxide (SO2) from exhaust gases. "Purifying" includes in this case also the recovery of buffers from a drawn off liquid flow. Such a drawing off is in many cases necessary in order to prevent impurities which accumulate in the process liquor, from building up to too high concentrations. The most important impurity will be sodium sulphate (Na2 SO4). but other components may also be present.

Impure solutions of the above type are for instance obtained when phosphate, citrate or adipate buffers are used for SO2 recovery from exhaust gases in coal heated boiler plants. In such uses SO2 is absorbed in the buffer solution to form bisulphite ions (HSO3-). In such process acidic hydronium ions (H3 O+) are liberated which are then taken up by buffer ions to form more of the acidic buffer components. The following reactions are utilized in the absorption plant when for instance phosphate ions represent the buffer system:

SO2 (g)=SO2(l) ( 1)

SO2 (l)+2H2 O(l) =H3 O+(l) +HSO3-(l) ( 2)

H3 O+(l) +HPO42-(l) =H2 PO4-(l) +H2 O(l) ( 3)

SO2(g) +H2 O(l) +HPO42-(l) =HSO3-(l) +H2 PO4-(l)

From the absorption tower the solution is conveyed to the regeneration plant, in which the liquid in this case is evaporated according to Norwegian Patent Application 85.3622. In the process SO2 is driven off together with vaporized water by reversing the reactions (1)-(3), and a concentration and precipitation of Na2 HPO4 takes place and possibly also of the oxidation product Na2SO4, as the buffers are usually employed in the form of Na salts:

NaHSO3(l) +NaH2 PO4(l) +nH2 O(l) =SO2(g) +(n+1)H2 O(g) +Na2 HPO4(s)

(n=a high number).

If citrate or adipate buffers are used instead of phosphate buffers, the regeneration does not take place by evaporation but by regular stripping with open steam in counter current towers. Then the regeneration takes place without any essential change in the liquid volume, by reversing the reactions (1)-(3), in which citrate ions and citric acid (Ci3-, HCi2-, H2 Ci-, H3 Ci) or adipate ions and adipic acid (Ad2-, HAd-, H2 Ad) are included in the reactions (3) instead of the phosphate ions (HPO42-, H2 PO4-).

For all said three processes the oxidation loss of SO2 is very small. Nevertheless, some increase of Na2 SO4 in the liquid must be expected, also because the gas from which SO2 is removed, often contains small concentrations of SO3 which are taken up by the buffer solution and which must be neutralized with a Na base (NaOH or Na2 CO3) An obvious possibility to maintain the Na2 SO4 concentration at an acceptable low level, would be to draw off a small flow of process liquid and replace this by fresh buffer solution. For a 500 MW power plant with 0.25 vol % SO2 in the exhaust gas and a sulphate formation corresponding to 0.25% of the amount of SO2, the amount of sulphate will amount to approx. 0.5 kmol/h. If it is desired to keep the sulphate concentration as low as 0.5 kmol/m3 only by removing process liquid, 1 m3 liquid per hour must be drawn off. With typically 3 moles per liter of Na2 HPO4 in the buffer at a price of approx. US $ 1.2 per kilogram, the loss of Na2 HPO4 alone will represent US $ 511 per hour. Even with this low estimate for the sulphate formation, such a drawing off of process liquid to remove Na2 SO4 from the system will lead to unacceptably high losses of Na2 HPO4. In addition it may represent considerable environmental problems. This illustrates that there exists a need for being able to remove Na2 SO4 selectively from the process liquid, i.e. without losing essential amounts of valuable buffer.

The buffer systems discussed herein are all salts of polyvalent acids. The SO2 uptake in the absorption tower displaces the buffer systems towards the more acidic buffer components. When reference is made to a selective removal of Na2 SO4, this means that no buffer components must be lost in essential amounts together with the Na2 SO4 removed. This is a problem to which it has been very difficult to find a satisfactory solution so far, as demonstrated for two cases:

In a known process for SO2 recovery from exhaust gases, SO2 is absorbed in an aqueous Na2 SO3 solution to form NaHSO3 :

SO2(g) =SO2(l)

SO2(l) =Na2 SO3(l) +H2 O(l) =2 NaHSO3(l)

The solution is regenerated by evaporation, whereby SO2 is separated and solid Na2 SO3 crystallizes:

2 NaHSO3(l) +n H2 O(l) =SO2(g) +(n+1)H2 O(g) +Na2 SO3(s)

(n=high number).

After dissolution of Na2 SO3(s) the buffer is ready for new absorption. For this "sulphite process" relatively high SO2 losses by oxidation are reported. Na-base is added to neutralize the sulphuric acid formed, and in one modification Na2 SO4 is removed from the absorption solution by cooling crystallization at about 0°C The salt which is then taken out, is reported to contain a high concentration of valuable buffer salts (1). which are thereby lost. In a modification extra SO2 is added to convert all Na2 SO3 to NaHSO3 in order to improve the selectivity in the Na2 SO4 precipitation (2). In another modification Na2 SO4 is removed by evaporation crystallization at high temperature. It is reported that this modification produces crystals having a lower Na2 SO4 content than the cooling crystallization, which means that it is less selective (3).

Particularly in the evaporation method, solutions having very high salt concentrations will be obtained, and it is then not possible on the basis of solubility data for the individual salts to say, with a reasonable degree of certainty, which selectivity can be obtained. The same uncertainty must also be expected in connection with evaporation of solutions of other salt mixtures.

For the above mentioned citrate process, based on SO2 absorption followed by regular steam stripping, there has been developed a multistep method for removing Na2 SO4 from a drawn off flow of process liquid, whereby a very high selectivity is attained (Norwegian Patent 133.546):

Step 1: Removal of Na-citrate by evaporation crystallization.

Step 2: Removal of Na2 SO4 by cooling crystallization.

Step 3: Removal of remaining Na-citrate by evaporation crystallization.

It has been argued against this method that it requires extensive process control, and that sodium citrate must be precipitated by evaporation under vacuum (4). Similar problems and objections may also be expected when the method is used for purifying adipate and phosphate buffers instead of citrate buffers, and there is accordingly a need for a simpler method for removing Na2 SO4 selectively from spent buffer solutions.

Relevant buffer concentrations are 0.25-3.0M for citrate and adipate buffers, and 2.0-5.0M for phosphate buffers. It is normally desirable to keep the Na2 SO4 concentration at no greater than 2.0M, particularly in the range 0.1-2.0M.

On the basis of a comprehensive test program we have now found an unexpectedly simple method for selective removal of Na2 SO4. This method may be adapted to the phosphate, citrate and adipate processes described above. The method is based on our observations that the solubility of Na2 SO4 in solutions simultaneously saturated with Na2 SO4 and one of the buffer salts in question, Na2 HPO4, Na2 HCi or NaHAd, is low at high temperatures, while at the same time the solubility is high for the buffer salts. According to the invention there is provided a process for removing sodium sulphate from aqueous citrate, adipate or phosphate buffer solutions used for absorption of SO2 from exhaust gases, without essential loss of SO2 and valuable buffer components. The process is characterized in that the aqueous buffer solution is evaporated at a temperature close to its normal boiling point to precipitate sodium sulphate, and in that the precipitated sodium sulphate is separated from its mother liquor and subjected to a possible further treatment to separate and recover accompanying buffer salts. Evaporated SO2 and the solution from which the Na2 SO4 crystals have been separated, are returned to the main process. Buffer solutions which are subjected to treatment, may herein be buffer solutions coming from the absorption unit in which they have been charged with SO2, or already regenerated buffer solutions which have been made ready for new absorption. In particular for phosphate buffers the evaporation to remove Na2 SO4 may be combined with the previously mentioned evaporation in the main process, in such a way that only an adjusted part of the already evaporated concentrate is taken out for sulphate removal.

The process is demonstrated by the following three examples:

PAC Citrate buffer

Procedure:

A controlled and known flow of buffer solution is drawn off from the liquid circulation cycle, for instance after the stripping tower. The liquid is evaporated at elevated temperature, i.e. substantially higher than in the first step of the above process for purifying citrate buffers, suitably at 100°C and atmospheric pressure. During this process Na2 SO4 crystallizes selectively. The evaporation is terminated before the Na-citrates have reached their saturation concentration. The evaporation may either be carried out as a continuous or as a discontinuous process. Crystallized Na2 SO4 is separated from the mother liquor which is returned to the main process, while the escaping steam, which will contain some SO2, may for instance be combined with the SO2 -containing exhaust steam from the stripping tower, so that SO2 values are not lost. Precipitated Na2 SO4 may thereafter be subjected to a new process step in which accompanying buffer components are dissolved in water at elevated temperature and conveyed back to the main process before the final removal of Na2 SO4.

The method is demonstrated in the following by evaporation of a Na2 HCi-rich buffer, but may also be used on buffer solutions rich in NaH2 Ci and H3 Ci. The latter buffers may be useful in the citrate process for purification of particularly SO2 -rich gases.

______________________________________
Data illustrating the usefulness
______________________________________
Volume of buffer solution drawn off:
1000 ml
Composition: 1.00M Na2 CHi +
0.5M Na2 SO4
Density of buffer solution:
1.19 g/ml
Calculated starting composition:
Na2 HCi: 19.8% by weight
Na2 SO4 : 6.0% by weight
______________________________________

This solution was evaporated at atmospheric pressure. The evaporation was carried out in a glass flask equipped with a water cooled condenser and a flask for collection of the condensate.

Evaporated amount of water was measured to: 768.0 g

Samples were then taken of crystal-free mother liquor for analysis. Weight and volume of the samples were determined before the samples were analyzed with respect to Na, P and S. The following results were obtained for samples taken at 100°C:

______________________________________
S Na C Density (g/ml)
______________________________________
Sample 1 0.46 12.98 21.12 1.49
(g/100 g sample)
Sample 2 0.68 11.86 18.91 1.44
(g/100 g sample)
______________________________________

From the S- and C-analyses the salt concentrations are calculated to be:

______________________________________
Na2 SO4
Na2 CHi
______________________________________
Sample 1 (g/100 g)
2.04 69.23
Sample 2 (g/100 g)
3.01 61.97
______________________________________

It is calculated that the salt concentrations found in this way correspond to an amount of Na in the samples of 14.2 and 12.3 g/100 g sample, respectively. The Na-analyses are in conformity with these values within reasonable limits of error.

The Na-analyses are considered to be the least accurate of the analyses made.

Mean value for the two samples give for the mother liquor:

65.5% by weight Na2 HCi

2.5% by weight Na2 SO4

ρ=1.47 g/ml.

In comparison the solubility of Na2 SO4 in pure water of 100°C is given as 29.7 g/100 g solution (5), i.e. about 12 times higher than that found in the mother liquor.

Remaining H2 O in mother liquor:

(1190-(1.00·236.1+0.50·142)-768.0=114.9 g

From this the following is calculated: ##EQU1##

Based on the above the precipitates as percentages are calculated: ##EQU2##

In the above example it is assumed that Na2 SO4 is precipitated by evaporation of the buffer solution taken from the flow after the SO2 stripping. It is also possible to precipitate sulphate by evaporation of a SO2 -rich solution drawn off from the process liquor which is conveyed to the stripping tower. However, this may entail a somewhat greater risk of corrosion.

PAC Adipate buffers

Procedure:

Process liquor for Na2 SO4 removal may in this case suitably be drawn off from the flows of process liquor immediately before the absorption column, i.e. after SO2 has been removed by stripping and after free adipic acid (H2 Ad) has been removed by cooling crystallization from the return liquid from the stripping tower. (The precipitated adipic acid is returned to the process liquid before stripping to facilitate the removal of SO2, see Norwegian printed specification 155684). Further processing is conducted according to the description from the citrate process.

______________________________________
Data illustrating the usefulness
______________________________________
Volume of buffer solution drawn off:
1000 ml
Composition: 1.00M NaHAd +
0.50 M Na2 SO4
Density of buffer solution:
1.11 g/ml
Calculated composition:
6.4% by weight
of Na2 SO4.
______________________________________

This solution was evaporated at atmospheric pressure.

Amount of water evaporated off: 790.4 g.

The mother liquor was then analysed as described for the citrate buffer, with the following result:

0.13 g S/100 g of sample

7.45 g Na/100 g of sample

28.64 g C/100 g of sample

density ρ=1.21 g/ml.

On the basis of the S- and C-analyses the following salt concentrations are found:

66.8% by weight of NaHAd

0.58% by weight of Na2 SO4

These salt concentrations correspond to a total Na-concentration of 9.33 g/100 g sample. This differs from the analysis by about 25%, which is more than expected on the basis of the assumed uncertainty of the analyses. (As previously mentioned the S- and C-analyses are considered more accurate than the Na-analysis).

Remaining H2 O:

(1110-(1.00·168.1+0.50·142))-790.4=80.5 g

From this the following is calculated:

______________________________________
Weight of mother liquor:
(80.5/(100 - 66.8 - 0.58))
100 = 246.6 g
Na2 SO4 in mother liquor:
246.8 · 0.00058 = 1.43 g
NaHad in mother liquor:
246.8 · 0.668 = 164.9 g
Percentage precipitated:
Na2 SO4 :
100 - (1.43/142 · 0.5) 100 = 98.0%
NaHAd: 100 - (164.9/168.1) 100 = 1.9%.
______________________________________

In the example it is assumed that the sulphate precipitation takes place by evaporating the process liquid after the SO2 stripping and adipic acid removal. Alternatively sulphate may be precipitated from SO2 -rich liquid from the absorption tower and before the H2 Ad-addition. Evaporation of adipic acid rich solution taken from the flow before or after the stripping tower is also a possibility, but there is a risk of coprecipitation of adipic acid which must be avoided.

PAC Phosphate buffer

Procedure:

The evaporation for regeneration of the process solution in the absorption-stripping-cycle may take place in two steps by allowing the liquid to pass in series or parallel through the two steps, and the exhaust steam from one of the steps serves as a heating medium for the other step (="double effect" evaporation). During the work with the invention it has been found that the precipitate is surprisingly rich in Na2 SO4, in particular this applies to the precipitation in the first step where the steps are arranged in series, and it is sufficient to take out a small part of this precipitate to keep the Na2 SO4 concentration in the process liquid at a desired level. Co-precipitated amounts of Na2 HPO4 and Na2 S2 O5 will be very small and will normally not represent any values of importance. However, the invention also comprises an unexpectedly simple embodiment in which the co-precipitated salts may generally be separated from Na2 SO4 so that the buffer salts may be returned practically quantitatively to the main process.

______________________________________
Data illustrating the usefulness
______________________________________
Start solution 2.50M Na2 HPO4
0.10M NaH2 PO4
0.50M Na2 SO4
1.49M SO2
V = 2.70 l
ρ = 1.37 g/cm3.
______________________________________

The composition corresponds here to a SO2 charged buffer from the absorption tower.

The solution is evaporated at atmospheric pressure, and precipitated salts are separated from the mother liquor by filtration in a pressure filter at 100°C, after the majority of the mother liquor has been removed by decanting clear liquid. The evaporation of decanted liquid is continued together with filtrate for new precipitation, etc. The composition of the filter cakes are then found on the basis of analysis of samples with respect to Na, P, total S and SIV -content, after dissolution in water.

Results:

______________________________________
Evaporation steps
1 2 3 Sum 1-3
______________________________________
(a)
Weight at the start
3699 2471.3 2186.7
of the evaporation (g)
(b)
Evaporated before
1131.8 120.7 238.4 1490.9
filtration
H2 O + SO2 (g)
(c)
Filter cake, 50.1 111.1 108.8 270.0
total weight (g)
Na2 SO4 (g)
28.4 55.4 41.2 125.0
Na2 HPO4 (g)
9.9 25.6 34.1 69.6
Na2 S2 O5 * (g)
6.7 15.2 16.2 38.1
(d)
Weight of decanted
2471.3 2186.7 1807.0
liquid and filtrate (g)
(e)
Not found
(a) - ((b) + (c) +
45.8 52.8 32.5
(d) (g)
______________________________________
*Na2 S2 O5 is an anhydride of NaHSO3 which only exist
in dissolved form.

Material which has not been recovered represents 1.2-2.1%, and is presumably due to loss of slurry and small amounts of steam and SO2 during the filtration.

From this the following is calculated:

______________________________________
Precipitated Na2 SO4,
(125/2.7 · 0.5 · 142) 100 = 65%
proportion of initial amount
1) Proportion by weight of
(125/270) 100 = 46%
Na2 SO4 in the filter cake:
2) Proportion by weight of
(69.6/270) 100 = 26%
Na2 HPO4 in the filter cake:
3) Proportion by weight of
(38.1/270) 100 = 14%
Na2 S2 O5 in the filter cake:
Sum 1) + 2) + 3) = 86%
______________________________________

The missing 14% is assumed to be primarily water. It is remarked that the filter cakes were not washed. Washing would have contributed to reduce the content of phosphate and disulphite in the cakes, since some mother liquor has been included in the analysis.

With reference to the power plant example discussed initially, the maintenance of 0.50M Na2 SO4 in the process liquid will in this case require a salt removal of X kg/h, in which

X·0.65/142=0.5 kmol Na2 SO4 /h.

From this follows: X=109 kg/h.

This removal is accompanied by

Na2 HPO4 : 109·0.26=28 kg/h

Na2 S2 O5 : 109·0.14=15 kg/h.

The value of the amount of phosphate is estimated on the basis of the price quoted above to 20·1.2=49 US $/h. This amount represents a negligible proportion of the costs connected with the SO2 process.

It it further remarked that totally 79.7 g SO2 and 1411.2 g H2 O have been removed by the evaporation in the example given. In comparison the content of H2 O in the initial solution is calculated to be:

2.7 (1370-(2.5·142+0.1·120+0.5·142+1.49·64 ))=2259 g.

According to this the amount of water evaporated off is:

(1411.2/2259)100=62 % of the initial amount.

Thus, the amount of water removed by evaporation is almost the same as that which would be suitable to evaporate in the first step in a two step evaporation process.

The example given herein was started with 0.1 mole/1 of the acidic buffer salt NaH2 PO4. It has been found that the method is equally suitable for higher concentrations of this salt. As an example, after evaporating off 1385.9 g H2 O+SO2 from a buffer with the initital composition 2.5M Na2 HPO4 +0.50M NaH2 PO4 +0.50M Na2 SO4 +1.20M SO2, 193.5 g of filter cake was filtered off, with a composition 48% Na2 SO4, 31% Na2 HPO4 and 18% Na2 S2 O5.

Examples 1-2 above illustrate very good selectivity for the sulphate precipitation from the citrate and adipate buffers respectively, while example 3 indicates a lower selectivity for the phosphate buffer. In particular when phosphate buffers are used, but also with adipate and citrate buffers, for instance when the process control is not as good as illustrated in examples 1 and 2, particularly so that the evaporation goes much further than illustrated above, an embodiment will therefore be desirable which ensures that a negligible proportion of buffer salts are lost together with precipitated Na2 SO4. In particular for the phosphate buffer this may be the case when the Na2 SO4 removal is started with finally evaporated and concentrated buffer/slurry from the regeneration part of the main process. It is thereby achieved that the removed Na2 SO4 has a high purity and thereby becomes simpler to sell commercially, or deposit. The essence of this part of the invention is that the Na2 SO4 precipitate from the evaporation step is subjected to a treatment with pure water at elevated temperature for selective solution of co-precipitated buffer salts. The solution which is thereby obtained is mixed with the rest of the buffer solution. The method is demonstrated with the following examples of results in laboratory experiments.

PAC Citrate buffer
______________________________________
Initial mixture of solid salts:
Na2 HCi
25 g
Na2 SO4
100 g.
______________________________________

This mixture corresponds to a sulphate precipitation from a too advanced evaporation.

40 g of H2 O were added to the "precipitate" in a closed glass flask equipped with stirrer, thermostated heating means, and a water cooled condenser for returning evaporated water. After 4 hours' treatment at 100°C a sample of clear liquid was taken out and analysed as explained above. Within the expected accuracy of analysis, 100% of the initial amount of NaHPO4 and 6.5% of Na2 SO4 were recovered in the resulting solution.

PAC Adipate buffer
______________________________________
Initial mixture NaHAd: 25 g
Na2 SO4 :
100 g
H2 O: 50 g
______________________________________

The experiment was carried out as described for the citrate buffer. The resulting solution was found to contain 100% NaHAd and 8.2% of Na2 SO4 in the initial mixture.

PAC Phosphate buffer
______________________________________
Initial mixture Na2 HPO4 :
50 g
Na2 SO4 :
100 g
H2 O: 90 g
______________________________________

The experiment was carried out as described for the citrate buffer. Within the accuracy of analysis the resulting solution was found to contain 100% of Na2 HPO4 and 14% of Na2 SO4 in the initial mixture.

The results in examples 4-6 illustrate that in this embodiment all the buffer will be recovered, while only Na2 SO4 will be removed from the system. The fact that some Na2 SO4 will accompany the buffer is insignificant, since there is no need for or desire to remove Na2 SO4 completely, but only to keep the Na2 SO4 concentration in the buffer solution at a suitably low level.

(1) NATO-CCMS STUDY. PHASE 1.1. Status Report on the Sodium Sulfite Scrubbing Flue Gas Desulfurization Process. US EPA, Washington DC. PEDCO Environmental, Cincinnati, Ohio. Contract No 68-01-4147, August 1978.

(2) DE-OS 25 06 666

(3) Pedroso, R. I. and Press, K. M. Sulphur recovered from flue gas at large coal fired power plants. In: "The Control of Sulphur and Other Gaseous Emissions", p F1-F20. 3rd Int. Symp., Salford (UK) 1979. EFCE Publ. Series No. 4.

(4) Keeth, R. S., Ireland, P. A. and Moser, R. E. Economic Evaluation of 24 FGD-Systems. EPA/EPRI FGD Symposium. Atlanta, Ga., Nov. 18-21, 1986.

(5) Ullmann 4. Auflage, Band 17, p. 211.

Erga, Olav

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